Member State report / Art8 / 2018 / D1-F / Spain / NE Atlantic: Bay of Biscay & Iberian Coast

Report type Member State report to Commission
MSFD Article Art. 8 Initial assessment (and Art. 17 updates)
Report due 2018-10-15
GES Descriptor D1 Fish
Member State Spain
Region/subregion NE Atlantic: Bay of Biscay & Iberian Coast
Reported by Subdirección General para la protección del mar. D.G. Sostenibilidad de la Costa y del Mar. Minister
Report date 2020-02-03
Report access msfd2018-ART8GES_MOD2020.xml

Demarcación marina noratlántica (ABI-ES-SD-NOR)

GES component
D1-F
Feature
Demersal shelf fish
Element
Argentina sphyraena
Arnoglossus imperialis
Arnoglossus laterna
Blennius ocellaris
Boops boops
Buglossidium luteum
Callionymus lyra
Callionymus maculatus
Capros aper
Cepola macrophthalma
Chelidonichthys cuculus
Chelidonichthys lucerna
Chelidonichthys obscurus
Conger conger
Eutrigla gurnardus
Gadiculus argenteus
Gaidropsarus macrophthalmus
Galeus melastomus
Helicolenus dactylopterus
Lepidorhombus boscii
Lepidorhombus whiffiagonis
Lesueurigobius friesii
Leucoraja naevus
Lophius budegassa
Lophius piscatorius
Merluccius merluccius
Microchirus variegatus
Micromesistius poutassou
Mullus surmuletus
Pagellus acarne
Phycis blennoides
Raja clavata
Raja montagui
Scorpaena loppei
Scyliorhinus canicula
Scyliorhinus stellaris
Serranus cabrilla
Solea solea
Trachinus draco
Trachurus trachurus
Trisopterus luscus
Trisopterus minutus
Zeus faber
Element code
126716
127124
127126
126761
127047
127153
126792
316815
127419
126835
127259
127262
127263
126285
150637
126435
126456
105812
127251
127145
126716
126904
105876
126716
126555
126484
127472
126439
126986
127057
126716
105883
105887
127244
105814
126716
127041
127160
127082
126822
126445
126446
127427
Element code source
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
ICES
Criterion
D1C1
D1C2
D1C3
D1C4
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
Parameter
Abundance
Biomass
Other
Distribution (range)
Parameter other
AVERAGE SIZE
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend
Unknown
Stable
Stable
Parameter achieved
Unknown
Yes
Yes
Description parameter
in general, a very high variability in time, and how in a number of cases there are significant changes in the trend of the first cycle to the second, but it is difficult to assess on a case-by-case basis and the 6-year cycle compared to the 20 years of the previous cycle does not make it easy to draw clear conclusions.
This indicator has been calculated for each sampling year, in this case 2011 to 2017, for a fixed species group. The species in this group are the same species as used in the other D1 indicators as in the D1C2 or D1C4 evaluation. The species have been grouped according to the size in ‘large’...
The species not meeting the criteria for increase/stability in the range are 5 in total, in particular 4 susceptible species and one opportunistic approach. With these results, there is still no result that differs from natural variability, therefore it would be within the BEA as maintenance of the proportion of species that meet the proposed criteria.
Related indicator
Criteria status
Not assessed
Unknown
Good
Good
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Description criteria
Species not commercially exploited: This indicator should be applied in the case of species and stocks that are not subject to catches by commercial fleets, such as marine mammals, turtles or seabirds. See explanation below on the reasons for not applying in the case of fish and demersal cephalop...
The results obtained in the previous evaluation have been updated by analysing all the data from the campaigns carried out from 2011 to 2017 in terms of abundance and biomass of the stocks that are considered to be actually sampled in the campaigns. The indicators have been estimated on the basis...
A good number of species showed a stable pattern (c.ca. 26 out of a total of 43). Considering that the indicator responds to fishing pressures and whereas the majority of these species were stable, it was possible to say that, although the trend towards growth was not significant, the stability o...
evolution of the percentage of grid blocks of 10x10nm with the presence of the species and assessment of the proportion of windows that meet the stipulated criteria to assess the extent to which the results fall within the natural variability or exit from what can be expected. The BEA is reached...
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description element
Integration rule type parameter
Not relevant
Integration rule description parameter
Integration rule type criteria
Not relevant
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
Unknown
Description overall status
Assessments period
2011-2017
Related pressures
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Related targets
  • A.N.1
  • A.N.10
  • A.N.11
  • A.N.2
  • A.N.3
  • A.N.5
  • A.N.6
  • A.N.7
  • A.N.8
  • A.N.9
  • B.N.14
  • B.N.15
  • C..N.9
  • C.N.15
  • C.N.16
  • C.N.17
  • C.N.18
  • C.N.3
  • C.N.4
  • C.N.6
  • C.N.7
  • C.N.8

Demarcación marina sudatlántica (ABI-ES-SD-SUD)

GES component
D1-F
Feature
Demersal shelf fish
Element
Argentina sphyraena
Arnoglossus imperialis
Arnoglossus laterna
Arnoglossus rueppelii
Arnoglossus thori
Boops boops
Callionymus maculatus
Cepola macrophthalma
Chelidonichthys obscurus
Citharus linguatula
Deltentosteus quadrimaculatus
Diplodus annularis
Diplodus bellottii
Diplodus vulgaris
Etmopterus spinax
Gadiculus argenteus
Galeus melastomus
Gnathophis mystax
Gobius niger
Helicolenus dactylopterus
Lepidotrigla cavillone
Lepidotrigla dieuzeidei
Lesueurigobius sanzi
Merluccius merluccius
Microchirus azevia
Microchirus boscanion
Microchirus ocellatus
Microchirus variegatus
Micromesistius poutassou
Mullus surmuletus
Pagellus acarne
Pagellus bellottii
Pagellus erythrinus
Phycis blennoides
Scorpaena notata
Scyliorhinus canicula
Serranus hepatus
Spicara flexuosa
Spondyliosoma cantharus
Symphurus nigrescens
Trachinus draco
Trachurus mediterraneus
Trachurus trachurus
Element code
126716
127124
127126
127127
127128
127047
126793
126835
127263
127130
126880
127049
127050
127054
105913
126435
105812
126287
126892
127251
127264
127264
126906
126484
274299
127470
127471
127472
126439
126986
127057
127058
127060
126501
127246
105814
127042
302566
127066
127134
127082
126820
126822
Element code source
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Species (D1) http://www.marinespecies.org/
Element 2
Element 2 code
Element 2 code source
Element source
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
Criterion
D1C1
D1C2
D1C3
D1C4
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
D1C1
D1C5
Parameter
Abundance
Biomass
Age distribution
Distribution (range)
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend
Unknown
Unknown
Stable
Parameter achieved
Unknown
Unknown
Yes
Description parameter
in general, a very high variability in time, and how in a number of cases there are significant changes in the trend of the first cycle to the second, but it is difficult to assess on a case-by-case basis and the 6-year cycle compared to the 20 years of the previous cycle does not make it easy to draw clear conclusions.
This indicator has been calculated for each sampling year, in this case 2011 to 2017, for a fixed species group. The species in this group are the same species as used in the other D1 indicators as in the D1C2 or D1C4 evaluation. The species have been grouped according to the size in ‘largeâ€...
In the ecotype of fish for vulnerable species we are seen as two species showing an increasing trend in the period 1993-2011 now showing a decreasing trend, while two other species which were shown stable or decreasing, are now showing a growing trend. That is to say, in the overall computer syst...
Related indicator
Criteria status
Not assessed
Unknown
Unknown
Good
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Not assessed
Description criteria
Species not commercially exploited: This indicator should be applied in the case of species and stocks that are not subject to catches by commercial fleets, such as marine mammals, turtles or seabirds. See explanation below on the reasons for not applying in the case of fish and demersal cephalop...
The results obtained in the previous evaluation have been updated by analysing all the data from the campaigns carried out from 2011 to 2017 in terms of abundance and biomass of the stocks that are considered to be actually sampled in the campaigns. The indicators have been estimated on the basis...
Insufficient data A situation very similar to that of the first assessment is observed, being an indicator of status/trends, and the observed situation of stability cannot be said to be either in the BEA or that the situation is deteriorating as compared to the first assessment.
BEA is reached for this criterion, defined as the maintenance of the situation in terms of species meeting the defined trends, although for cephalopods the trend is growing in most species, these are short-lived species where the abundance is often very variable and in pulses without presenting problems for the whole ecosystem.
Element status
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Unknown
Description element
Integration rule type parameter
Not relevant
Integration rule description parameter
Integration rule type criteria
Not relevant
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
Unknown
Description overall status
Assessments period
1993-2017
Related pressures
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Related targets
  • A.N.1
  • A.N.10
  • A.N.11
  • A.N.2
  • A.N.3
  • A.N.5
  • A.N.6
  • A.N.7
  • A.N.8
  • A.N.9
  • B.N.14
  • B.N.15
  • C..N.9
  • C.N.15
  • C.N.16
  • C.N.17
  • C.N.18
  • C.N.3
  • C.N.4
  • C.N.6
  • C.N.7
  • C.N.8